copy the linklink copied!3. Coherence across national strategies and plans for sustainable land use
National strategies and plans establish a country’s medium- to long-term priorities across a range of sectors. This chapter analyses the extent to which land use, biodiversity, climate and food considerations are included in the strategies and action plans developed in the case study countries (Brazil, France, Indonesia, Ireland, Mexico and New Zealand). The chapter analyses the coherence between land-use relevant targets in Nationally Determined Contributions (NDCs) (developed in response to the Paris Agreement), long-term Low Emissions Development Strategies (LEDS), National Biodiversity Strategies and Action Plans (NBSAP) (developed in response to the UN Convention on Biological Diversity), Agricultural Development Plans, National Development Plans (or similar), National Forestry Plans and National Trade or Export Plans.
National strategies establish a country’s medium- to long-term priorities in various areas. They are intended to guide and steer national actions in particular sectors or policy areas. In some cases (notably for biodiversity), strategies also include associated action plans. National strategies, therefore, should develop, in a consultative manner, common objectives that various Ministries will need to work towards. National strategies should provide clear and actionable objectives that the national government – and all relevant Ministries – should be striving to achieve. To this end, strategies and action plans that set specific, measurable, time-bound targets, and that also identify indicators against which progress can be assessed, can strongly facilitate this process. Given the various potential synergies and trade-offs across sectors and policy areas, the various multiple strategies should be coherent with one another.
In some cases, the development of national strategies are encouraged or required by overarching international multilateral agreements or initiatives. This is true, for example, for National Biodiversity Strategies and Action Plans (NBSAPs) required under the Convention on Biological Diversity, or for National Strategy or Action Plans required for implementation of REDD+ under the UNFCCC. Nevertheless, even without international agreements in other areas of the land-use nexus, nearly all governments have established national agricultural strategies or plans, forestry plans, and overarching economic growth or development plans.
Key strategies and plans that are relevant to the land-use nexus include Nationally Determined Contributions (NDCs), long-term Low Emissions Development Strategies (LEDS), NBSAPs, Agricultural Development Plans, National Development Plans (or similar), and National Trade or Export Plans. This Chapter begins with a brief overview of the relevant multilateral agreements in the land-use nexus, and the requirements or guidelines to transpose these at the national level, thereunder. It then proceeds to compare relevant national strategies and plans across the six case study countries, to examine their degree of coherence.
copy the linklink copied!The role of multilateral agreements in guiding national strategies
At the international level, the 2030 Agenda and the Sustainable Development Goals have spurred efforts to examine, more holistically, how actions to achieve one goal may interact, both positively and negatively, to achieve others (outlined in chapter 1). The specific targets, as well as the indicators, set a framework for action across the multiple sustainable development areas, including the need for policy coherence (SDG 17). Similarly, though focussing on specific environmental areas, the UNFCCC and the CBD set the international framework for action on climate change and on biodiversity, respectively.1 These differ in various ways in terms of the information that countries are invited or required to submit, including with respect to national strategies and plans (Table 3.1), as well as the timelines covered.
Under the Paris agreement, Parties are required to submit NDCs stating their GHG emission targets. These NDCs are relatively short-term, with the first running until 2025 or 2030 (to be followed by subsequent NDCs). It is for countries to determine the level and sectoral coverage of such targets. Some of the NDCs include explicit references to forests2 and agriculture and may have associated targets, others do not.
The Paris Agreement, agreed in 2015, also invited Parties to submit, by 2020, long-term low GHG emissions development strategies to 2050 (Paris Agreement, Article 4.19).3 Ten countries had done so by February 2019, including France and Mexico.4 Given the longer-term nature of these strategies, it is more difficult for governments to establish specific action plans. Parties to the UNFCCC are also required to submit National Communications, which highlight, inter alia, climate policies and measures planned or undertaken. In addition, Annex I5 countries are required to outline progress towards their climate targets in biennial reports; a requirement extended in the Katowice Climate Package to all countries in the “biennial transparency reports” to be produced at latest by the end of 2024.
Under the CBD, the twenty 2011-2020 Aichi Biodiversity Targets include targets related to forests (Targets 5 and 7), agriculture (e.g. Targets 7 and 8), climate change (Targets 10 and 15)6, ecosystem services (Target 15) and many relate to land use more generally. Parties to the CBD are encouraged to use the Aichi Biodiversity Targets as a guiding framework to develop their NBSAPs.
As a result, the overarching CBD framework encourages a more coherent approach with respect to the development of NBSAPs and the land-use nexus at the national level, than does the UNFCCC. This is because as there are limited guidelines on what information to include in an NDC, and no requirements on the form or coverage it should take, there are wide variations in form, content and coverage. On the other hand, the timeframes for documents under this CBD framework are significantly more near-term (i.e. to 2020) than under the UNFCCC framework.
Other relevant agreements and fora
Other relevant international multilateral agreements include the UN Strategic Plan for Forests, developed by the United Nations Forum on Forests (UNFF) and subsequently adopted by the UN General Assembly in 2017. The Strategy contains six voluntary global forest goals and 26 associated targets to be achieved by 2030. Member States are invited to announce their “voluntary national contributions” towards achieving these goals and targets at upcoming sessions of the UNFF. As of 31 July 2018, five countries had submitted such announcements. At the supranational level, through the European Union, the 28 Member States are also governed by various EC Directives that are relevant to the nexus area. These include EU legislation on the Climate and Energy Package, EC Nature Directive, the Habitats Directive, the Sustainable Use Directive (for pesticides), the Water Framework Directive, and the Common Agricultural Policy (CAP). This supranational framework therefore strongly influences agricultural policy in France and Ireland.
SDG goal 12.3 directly addresses food loss and waste (FLW); “by 2030, halve per capita global food waste at the retail and consumer levels and reduce food losses along the production and supply chains, including post-harvest losses”, but beyond the SDGs international agreements tackling FLW are lacking. At the EU level the Waste Framework Directive defines a timeline for adopting common measurement methodologies and will produce a report by 2023 that considers the introduction of legally binding targets for food waste prevention (Champions 12.3, 2018[2]). There is also the EU Platform on Food Losses and Waste, which brings together key stakeholders from government, industry and NGOs to understand the issues of FLW, and highlight good practices from member countries. Despite several other international initiatives, such as the FAOs global initiative on Food Losses and Waste Reduction (SAVE FOOD), the integration measures to reduce FLW in other nexus relevant agreements, such as NDC or NBSAPs is lacking. Greater consideration of FLW in such agreements would likely raise the profile of this issue leading to emission savings and reduced pressure on managed and unmanaged lands and other impacts from agriculture.
copy the linklink copied!Coherence across key national strategies and action plans relevant to the nexus
As noted, coherence across relevant national strategies in the land-use nexus is a key entry point to help ensure that domestic actions and policies across multiple sectors and areas are aligned. Clear and quantified objectives can provide strong signals for the level of ambition that is necessary across different sectors and policy areas.
In what follows, the key national strategy documents across the six case study countries are compared and discussed. Overall, the analysis suggests that there is still large scope to strengthen coherence and clarity across the national strategies relevant to the land-use nexus. Few of the NDCs and LEDS refer to land-use nexus issues (e.g. forests, agriculture). Those that do specifically refer to the land-use nexus tend to provide quantitative targets, however, at least in selected areas (e.g. as in France, Indonesia and Mexico – see Table 3.2)
The monitoring of GHG emissions and removals from all sectors has already been underway for a number of years, and the indicator for GHG emissions, tCO2e, is well established, facilitating the creation of quantitative targets. In contrast, nearly all of the NBSAPs make reference and include some kind of target relevant to forestry, agriculture and climate change (as noted above, this is due, at least in part, to the overarching Aichi Biodiversity Targets that also refer specifically to these issues). While being more coherent in this general sense, many of the targets relevant to the land-use nexus in the NBSAPs are not quantified.
For example, New Zealand’s Target 7 to implement a national environmental standard for plantation forestry by 2018, and France’s target 3.2 to integrate biodiversity in forest management plans, do not provide clear direction on the level of ambition that is needed. In contrast, Brazil’s target to restore at least 15% of degraded land, and France’s target on zero net artificialisation provide much clearer signals to relevant Ministries on the objectives they are intended to achieve.
Agricultural development plans tend to be vaguer than NBSAPs with respect to land-use nexus issues. While pressures on climate change, biodiversity/ecosystems and forests are generally acknowledged across the plans of all six countries, the language therein is limited to phrases such as “improve efficiency”, “support efforts”, “minimise risk”. Given the large proportion of GHG emissions stemming from this sector, and the pressures that agricultural land use and management practices exert on biodiversity, the lack of specificity in these plans creates large potential for various Ministries to interpret the language in different ways, and for eventual policy misalignments. Ideally, relevant agriculture-relevant targets in, for example, the NBSAPs should also be reflected in the countries’ agricultural development plan. Such an approach would send consistent signals to the various Ministries in the land-use nexus.
References to land-use nexus issues in the National Development Plans (or similar strategies) are similarly ambiguous. New Zealand and Ireland are, to some degree, exceptions: New Zealand’s Economic Plan specifically calls for the planting of 1 billion trees, and Ireland’s plan refers to afforestation targets to rise incrementally by a quantified amount each year. A closer examination of the strategies is provided below.
Looking across the various national strategies and plans relevant to the nexus in Ireland indicates that there is significant coordination and integration between land-use, climate mitigation, ecosystems/biodiversity and food objectives. In all cases, the main documents in each policy area were created with input from one or more of the other areas. However, references to biodiversity/ecosystems in the agricultural development plans and the national development plan are fairly general. Despite this, its importance is recognised in all the key policy documents such as the National Mitigation Plan, Food Wise 2025, as well as the Rural Development Plan.
Ireland’s NBSAP is particularly clearly defined (i.e., in comparison to its other national strategies) in that it includes clear targets, actions and has also defined indicators in order to monitor progress towards achieving these (though some are SMARTer than others). The targets are cross-cutting, with specific references and measures relating to agriculture and forestry (e.g. NBSAP Target 4.1 and the actions thereunder, which refer to Agri-Environment Schemes, High Nature Value farmland, etc, and associated indicators). The role of Protected Areas in enabling adaptation to climate change is also recognised, with specific targets to increase peatland area. In contrast, Ireland’s National Development Plan (2018-2027) does not include specific (quantitative) targets and indicators. Mention to e.g. biodiversity is made, but it basically refers back to the NBSAP.
GHG mitigation targets in the NDCs and LEDS and the inclusion of land-use nexus issues
References to land-use, ecosystems and food security issues in the NDCs and LEDS across the six case study countries are compared in Table 3.2 providing an indication of the extent to which these issues are mainstreamed in national climate change strategies. Land-use issues, agriculture, and forestry are explicitly referred to in three of the six Parties’ NDCs (Brazil, Indonesia, and Mexico)7 with specific targets included for several of these. Looking across these three NDC’s, it is difficult to compare the relative ambition of these targets given the lack of consistency in the way they are expressed.8 Overall, explicit reference to interlinkages with biodiversity or ecosystems is made rarely in these documents.9
In addition to NDCs, certain countries have developed national strategies or plans that are more detailed. In France, for example, the National Low-Carbon Strategy (SNBC)10 was published in November, 2015, with a revised version published in 2018. It outlines strategic guidelines for implementing the transition to a sustainable, low-carbon economy across all sectors of activity including agriculture (see Table 3.2). It also highlights the importance of individual behaviour, including dietary changes, for reaching national GHG mitigation targets.
In addition, the Climate Plan (July 2017)11 specifies both long-term objectives and shorter term milestones and explicitly strengthens the French GHG 2050 target from ‘Factor 4’12 up to carbon neutrality. The Climate Plan, drawn up at the request of the President and Prime Minister, calls on all government departments across the board to step up the pace of the energy and climate transition and of the Paris Agreement's implementation. The Plan aims to foster coherence between climate change mitigation and land use, ecosystems and food. It focusses on these elements in its fifth part (‘Mobilising the potential of ecosystems and agriculture in order to tackle climate change’), from axis 15 to 19: axis 15 and 17 emphasise the importance of the sustainable management of forests to achieve climate ambitions, directly on the French territory (axis 17) but also through improved consumption to reduce deforestation (axis 15) (the latter is discussed below).
Inclusion of land-use nexus issues in the NBSAPs
Overall, fewer countries have specific targets relating to forest and agriculture in their (climate) NDCs and LT-LEDS, than specific targets relating to climate, forest and agriculture in their national biodiversity strategies. Table 3.3 summarises the information on forestry, agriculture and climate change in the National Biodiversity Strategies and Action Plans. While all NBSAPs refer to various areas of the land-use nexus however, a review of the six NBSAPs indicates that often these references are not specific, not ambitious or both (e.g. Indonesia: “improvement of forestry areas”; Ireland: “continue forest research programmes”). Most of the targets are not quantified and hence do not provide sufficiently specific guidance for relevant Ministries to act. Exceptions include France for some of their targets such as on zero net artificialisation of land13; Brazil, with respect to the target to restore at least 15% of degraded land, and Ireland, with a target to achieve 30% broadleaf afforestation.
The lack of quantification of many of the targets also implies that they are not measurable. Several of the NBSAPs do include the use of indicators with the targets, namely those of Brazil, Indonesia, Ireland and France; some are more specific than others however. Brazil brought together nearly 280 institutions to develop its NBSAP, and established a multi-stakeholder Panel for Biodiversity (PainelBio) to develop the indicators. Mexico and New Zealand do not include indicators. Overall, it is very difficult to guide national action in a coherent, transparent way if targets are not specific, measurable, actionable, realistic and time-bound (SMART).
Some of the case study countries’ NBSAPs moreover refer to the protection of certain core forested areas (Brazil) or “stewardship lands with high conservation value” (New Zealand), and to targets to reduce and curb forest (Mexico, Brazil) or habitat (Ireland, France) fragmentation. Action 7 under Target 5 of the Brazilian NBSAP, for instance, is to “reduce fragmentation of remaining forest patches, as well as promote the connection of forest fragments”. Related targets, however, mostly remain qualitative.14
France has also developed a National Forests and Woodlands Programme (MAA, 2016[6]), proposed by the MAA and adopted in 2016, which defines the main objectives of the French forest policy for the 2016-26 timeframe. It notes the role of forests in reducing GHG emissions, and the interrelations between biodiversity and climate change policies. Similarly, Ireland’s Department of Agriculture, Food and the Marine developed in 2014 a forest policy strategy in its document “Forests, products and people, Ireland’s forestry policy – a renewed vision”. This includes a cost-benefit analysis of future afforestation programmes, where the benefits considered include timber, carbon sequestration, biodiversity, water quality, among others.
The Aichi Biodiversity Targets also explicitly recognise the need to eliminate, phase out or reform incentives, including subsidies, harmful to biodiversity under its Target 3. Nevertheless, very few of the NBSAPs refer to incentives, including subsidies, harmful to biodiversity, despite market-distorting and potentially-harmful subsidies being in place in all the case study countries (see chapter 5). Similar language on reforming harmful incentives is also in the reporting guidelines for national communications on climate change, yet few countries have done this. Identifying and assessing existing incentives that are not coherent with international environmental goals is a key first step. Commitments to undertake these assessments, such as through national assessments (e.g. France and biodiversity) or international peer-review processes (e.g. Indonesia fossil fuel subsidy G20 peer-review) are an important first step.
Such commitments include Ireland wherein the NBSAP states they will undertake a study in the 2017-2019 timeframe, and Brazil, which takes on Aichi Target 3 at national level nearly verbatim, stating that by 2020, at the latest, incentives harmful to biodiversity, including the so-called perverse subsidies, are eliminated, phased out or reformed.15 More specifically for Ireland under Target 1, Action 1.1.15. is to: Identify and take measures to minimise the impact of incentives and subsidies on biodiversity loss, and develop positive incentive measures, where necessary, to assist the conservation of biodiversity. The performance indicator defined is: 1. Policies and practices that generate perverse incentives identified; 2. Number of appropriate reform policies designed and implemented. This language presents a clear, time-bound commitment to tackle this issue. In contrast, in France, while a report on domestic public subsidies harmful to biodiversity has already been undertaken (CAS, 2011[7]), it is not referred to in the NBS nor the NBP.
In Brazil, some states, including São Paulo, Paraná and Rio Grande do Sul, have also developed biodiversity strategies and action plans or programmes. However, ensuring consistency and synergy with the federal biodiversity policies, programmes and targets has been challenging (OECD, 2015[8]).
Inclusion of land-use nexus issues in agricultural development plans
In contrast to climate change and biodiversity, there is no overarching multilateral agreement that requires or invites governments to develop national agricultural development plans. Nevertheless, most (if not all) countries have developed such strategies. For France and Ireland, agricultural policies are determined, to a large extent at the European level, by the CAP. Table 3.4 summarises the references to climate mitigation, forestry, and biodiversity/ecosystems in the national agricultural development plans (or other similar national documents).
Looking across the six countries and the nexus areas, only Brazil has clearly defined actions, together with quantified targets in the context of climate mitigation. While references to the nexus areas are made in nearly all of the six countries’ agriculture development plans, these are all fairly general.
France has however developed a Plan for Agroforestry Development for 2015-2020, released in 2015 by the MAA (Government of France, 2015[16]). This presents actions to encourage farmers to adopt practices coupling trees, crops and farming. It underlines the role hedges and trees play for timber and fodder production, limiting erosion, waterborne and microclimate regulation, carbon storage or climate change adaptation. The Plan argues for research and development and a better understanding of agroforestry systems, a better regulatory framework and stronger financial incentives, and the development of a national sector enhancing the economic value of agroforestry by-products. It also includes the promotion of agroforestry at an international level as an objective. None of the actions outlined, however, have clear specific targets associated with them.
Inclusion of land-use nexus issues in national development plans (or similar strategies)
Perhaps the politically weightiest and overarching national strategies are the national development plans (or similar documents). References to the land-use nexus issues across these documents are compared in Table 3.5. France does not have a national development plan per se, but rather has established a National Strategy for Sustainable Development which covers all aspects of the land-use nexus and makes the case for action. It does not, however, lay out specific targets to be achieved.
Indonesia’s Master Plan for Economic Development 2011-2021 (the long-term plan) does not refer to the environmental impacts of the development (other than as a side-effect of the growth in palm oil production). However, the medium-term development plan (RPJMN 2015-2019) does refer to forest conservation and the NBSAP. The importance of environmental issues, including ecosystems and climate change, are recognised in Indonesia’s development planning process. The long-term development strategy set for 2005-2025 recognises environmental sustainability as one of the nine development missions for Indonesia to pursue. It also has the aim of exploiting Indonesia's comparative advantage in agriculture and mining to achieve food self-sufficiency and middle-income status by 2025. The RPJMN is based on the concept of the green economy, specifying concrete targets for achieving the overall missions set out in the long-term strategy.
The next phase of the medium-term national development plan (RPJMN 2020-24) provides an opportunity to ensure greater effort to reconcile the specific goals of developmental policy with the climate change, land use and ecosystems targets. As part of the preparations for the future RPJMN 2020-2024, BAPPENAS undertook modelling to strengthen coherence between relevant sectoral targets and to facilitate discussion between stakeholders. The elaboration of sectoral targets, however, does not appear to have fully considered interactions between objectives. Given that there is only a finite stock of land, the implicit demands for land from each objective need to be consistent. Increases in production will require a combination of increased productivity and increased land area. The consequences for ecosystems and climate depends on where expansion occurs. However, the production objectives for food and energy crops make claims on degraded land and convertible production forest.
Ireland’s NDP refers to multiple aspects of the land-use nexus and defines investment priorities that include references to these areas. It also provides indicative (monetary) resource allocations for delivery of the various National Strategic Objectives thereunder. While resource allocation is quantitative by definition, since this is an input indicator, rather than an outcome or impact indicator, it will be difficult to determine whether progress is being made towards the ultimate objectives of the NDP in relation to the land-use nexus.
Brazil’s Multi-Year Plan (Plano Plurianual (PPA) 2016-2019), on the other hand, defines both monetary inputs dedicated to specific government programmes and overarching objectives along with detailed, quantitative programme targets and indicators. Among the 54 strategic government programmes set out in the PPA, topics of relevance to the land-use nexus figure prominently. Various programmes pertain to agriculture and food security (i.e. programmes 2012, 2066, 2069) and set quantitative targets relating to, inter alia, the provision of rural credit, technical assistance and extension services, the registration and regularization of forest and agricultural land, the expansion of support to agroecological practices in family agriculture, and food assistance and school feeding programmes. Specific programmes are devoted to climate change mitigation and adaptation action (Programme 2050: Climate Change) and the protection of biodiversity (Programme 2078: Conservation and Sustainable Use of Biodiversity). Notable targets specified for these programmes include: (i) absolute emissions reductions from reduced deforestation in the Amazon region of 737,465,122 tCO2e (target 047B) and of 70,000,000 tCO2e from the agricultural sector against baseline projections (target 047E); and (ii) the reduction of the risk of extinction of 20% of the species listed in the Official National List of Species threatened by extinction (target 4084). The PPA moreover designates the government ministry responsible for the delivery of the specified objectives and targets.
In New Zealand, the Ministry for Primary Industries (MPI) has set out a strategy for achieving its purpose of “Growing and Protecting New Zealand” (MPI, 2017[24]). This strategy comprises four key outcomes, the first of which is growth in production and the second is sustainability. Ecosystems and climate change are not explicitly mentioned in this strategy (though they could be seen as implied by the sustainability objective). The MPI also reports on its performance. The MPI “Strategic Intentions 2015-2020” includes indicators for measuring progress, including on sustainability. These indicators refer most predominantly to water, nutrient management and fisheries. There is no specific reference to biodiversity in the document.
Looking beyond national jurisdictional boundaries: Consideration of land-use nexus issues in trade policy
Given the close interlinkages between land-use outcomes and international trade it is important that trade policy is coherent with sustainable land use. Commonly conceived of as a driver of economic growth, international trade receives significant policy attention across the case study countries. While the promotion of international trade is part of most of the overarching national development plans or strategies, few of these explicitly acknowledge interactions of trade and land-use nexus issues (table 3.6).
Similarly, most of the case study countries’ trade or export strategies and plans do not explicitly account for the land-use nexus implications of trade policy. For most countries, these documents provide further detail of the plans for trade in nexus-relevant products (Table 3.7). However, while the plans and strategies that do so primarily lay out sub-targets and strategies to grow agri-food exports, only some make limited reference to the attainment of environmental objectives, or domestic (Indonesia) or international (Brazil) food security objectives. The relative lack of consideration of land-use nexus issues in general trade policy represents a potential challenge to policy coherence.
This is true also in countries where dedicated initiatives to tackle adverse land-use nexus impacts of international trade exist already. France and Ireland have noteworthy initiatives aimed at addressing these impacts.16 France, for instance, has a National Strategy to Combat Imported Deforestation (SNDI)17 (Ministère de la transition écologique et solidaire, 2018[25]) in place. As announced under Axis 15 in its Climate Plan, the SNDI was developed in 2018 in a consultative manner by the French Ministry of Agriculture, in collaboration with the French Ministries of the Environment, Foreign Affairs, Economy, and Research and Innovation, and the involvement of all stakeholders gathered in the National Group on Tropical Forests (GNFT). The GNFT, has itself been recently expanded to include representatives of the agri-food sector. The SNDI is intended to contribute to several international goals on climate and forest (i.e., the SDGs, New York Declaration on Forests, Paris Agreement, Amsterdam declarations). Its main orientations are to increase cooperation with producer countries, systematically integrate deforestation in public policies, mobilise and empower the private sector and develop research. The SNDI also aims to establish a national platform to provide reliable information on imported deforestation, value commitments, and help the private sector monitor its commodities supply chains through an early alert mechanism. As France is among the top 10 timber importers globally, this initiative is potentially important globally (for more detail on the SNDI, see also Chapter 5).
In a similar vein, Target 7.4 in Ireland’s NBSAP is: Reduction in the impact of Irish trade on global biodiversity and ecosystem services. More specifically the action identified is 7.4.1. “Adopt measures to significantly reduce negative impacts of trade on biodiversity and to enhance positive impacts”. The lead agencies tasked with this action are clearly defined (i.e., DCHG, DFAT, DAFM), and two indicators have been identified to assess progress towards this: 1. Knowledge of the pressures placed on biodiversity by trading activity and trade routing; and 2. Measures implemented to reduce or offset those pressures and their impacts. The progress on this initiative is unclear but, if successful, it could serve as a model for other countries considering the same approach.
While these initiatives are laudable from an nexus perspective, their impacts will be constrained if the policies recommended are not mainstreamed into general trade policy. Despite the existence of a dedicated strategy in form of the SNDI, the French Government Foreign Trade Strategy (Premier Ministre de la République Francaise, 2018[26]) does not acknowledge land-use nexus impacts of French trade policy.
Mainstreaming of land-use nexus issues in trade policy formulation and implementation therefore represents a necessary and promising avenue for improved land-use outcomes and greater policy coherence. In order for trade policy to effectively reduce land-use impacts abroad (including by pursuing quantitative targets that would complement export growth targets), a quantitative understanding of the nature and magnitude of these impacts should be gained (Chapter 5) and considered in trade policy formulation.
References
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Notes
← 1. Under the UNFCCC’s Paris Agreement, there is an overarching goal of limiting global warming to well below 2 degrees of warming, with the agreed objective to pursue efforts to keep warming well below 1.5 degrees. Under the CBD, a guiding framework has been agreed upon, with 20 Aichi Biodiversity Targets. Parties are encouraged, but not required, to use the Aichi Biodiversity Targets as a framework for developing their own national strategies and associated targets.
← 2. Article 5 of the Paris Agreement states Parties should take action to conserve and enhance, as appropriate, sinks and reservoirs of GHGs, including forests. It also encourages Parties to take action relating to REDD.
← 3. Parties were also encouraged to do this at COP17 in 2011.
← 4. https://unfccc.int/process/the-paris-agreement/long-term-strategies
← 5. Parties include the industrialized countries that were members of the OECD (Organisation for Economic Co-operation and Development) in 1992, plus countries with economies in transition, including the Russian Federation, the Baltic States, and several Central and Eastern European States.
← 6. Target 15 states: By 2020, ecosystem resilience and the contribution of biodiversity to carbon stocks has been enhanced, through conservation and restoration, including restoration of at least 15 per cent of degraded ecosystems, thereby contributing to climate change mitigation and adaptation and to combating desertification.
← 7. NB: France and Ireland have country-wide targets, hence agriculture and forestry are included by definition.
← 8. Guidance on NDCs is currently being negotiated. The aim of such guidance is to facilitate clarity, transparency and understanding of NDCs.
← 9. According to Richards et al. (2015[32]) who examined 162 Party submissions, AFOLU is well represented in most Parties NDC’s and appears to be a key strategy for climate change mitigation in a majority of countries. Forest-related mitigation measures are even more frequently mentioned in Parties’ NDCs than agriculture, with 80% of the submitted NDCs including targets related to the LULUCF sector, compared to 64% that specifically included agriculture.
← 10. See https://unfccc.int/files/focus/long-term_strategies/application/pdf/snbc_4pager_fr_en.pdf
← 11. See (Government of France, 2017[33]) https://www.gouvernement.fr/en/climate-plan and https://www.ecologique-solidaire.gouv.fr/sites/default/files/2017.07.06%20-%20Plan%20Climat_0.pdf (Government of France, 2017[34])
← 12. Factor 4 specifies a 75% reduction in total GHG emissions in 2050 compared to 1990 levels.
← 13. This refers to activities that result in extensive sealing of the soil in unmanaged, agricultural or forest lands due to inter alia urban sprawl and transport infrastructure. The French objective is in line with the EU’s “zero net land take” objective (EC, 2011[35]).
← 14. In Brazil, a Landscape fragmentation and connectivity index that could potentially inform quantitative targets is currently under assessment for use in future iterations of the NBSAP.
← 15. Examples of potentially harmful subsidies that could be included in these assessments include concessional loans, preferential credit, market price support for soy and subsidised insurance for farmers that could encourage agricultural land conversion in Brazil, and distortive subsidies to unsustainable farming practices under the EU CAP in Ireland. More detail on potentially harmful subsidies along with examples from other case study countries is provided in chapter 5.
← 16. In a sense, France has adopted a sector-like approach, focusing on forests, whereas Ireland covers trade-related issues more generally, but for an environmental policy area, namely biodiversity.
← 17. Imported deforestation refers to imported products that are directly or indirectly the result of deforestation or forest degradation (e.g., wood coming from environmentally sensitive forests that have been chopped down; and products such as beef or palm oil that were produced in areas of slash-and-burn cultivation) (source: https://frenchfoodintheus.org/3977).
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