Abstract
How does the UN Convention on Biological Diversity (CBD) presently addresses the topic of soils? And what are potential ways of strengthening the integration of soils in the CBD agenda in the future?
The paper at hand reviews these questions. Firstly, we give a brief overview of the international governance of soil sustainability to date, locating the role of the CBD in this context. Secondly, we elaborate on how the CBD addresses soil (biodiversity) issues—e.g., in its Strategic Plan and Aichi Targets, through principles for the sustainable use of biodiversity, the CBD’s Ecosystem Approach as well as the International Soil Biodiversity Initiative. In the discussion, we highlight the value and shortcomings of the soil topic under the CBD. We also develop options for strengthening sustainable soil management both within and through the CBD. We conclude that the CBD can indeed contribute to the political promotion of sustainable soil use but that there are presently few incentives for CBD parties to push the process forward. Also, to be effective, the CBD is dependent on meaningful progress in international politics on the broader topic of sustainable land use.
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Notes
- 1.
Weigelt et al. (2014).
- 2.
- 3.
European Commission (2006).
- 4.
In the literature, the distinction between soil management, soil use and land use is often unclear and blurred. We employ the terms “soil use” and “soil management” largely interchangeably, with a tendency to use “soil use” in a broader sense (referring to uses such as plant production, grassland management, soil use for residential settlements vs. industrial sites etc.) and “soil management” in a narrower sense (referring to more specific practices (mostly) to prevent soil degradation, like crop rotation, soil cover, tillage practices, afforestation, nutrient management, water retention etc.). By “land use” we mean broad categories such as agriculture, forestry, building land, mineral extraction etc.
- 5.
More specifically, FAO and ITPS (2015) set the following criteria for sustainably managed soils: leakage of nutrients is low; biological production is high relative to the potential limits set by climate and water availability; levels of biodiversity within and above the soil are relatively high; rainfall is efficiently captured and held within the root zone; rates of soil erosion and deposition are low, with only small quantities being transferred out of the system; contaminants are not introduced into the landscape and existing contaminants are not concentrated to levels that cause harm; systems for producing food and fibre for human consumption do not rely on large net inputs of energy; and net emissions of greenhouse gases are zero or less.
- 6.
Ginzky (2015).
- 7.
Lal (2004).
- 8.
IPCC (2014).
- 9.
Cf. the chapter by Boer et al. (2016).
- 10.
Altvater et al. (2015).
- 11.
UNEP/CBD/SBSTTA/7/INF/11.
- 12.
Jeffery et al. (2010), p. 8.
- 13.
Ibid.
- 14.
Wunder et al. (2013).
- 15.
Montanarella and Vargas (2012), p. 1.
- 16.
Held and Kümmerer (1997).
- 17.
The assessment which is due in 2018 will cover the global status of and trends in land degradation and ecosystem restoration (by region and land cover type). It will also identify the effects of degradation on biodiversity (including soil biodiversity), on ecosystem services (among others, soil formation, soil fertility, nutrient cycling, erosion prevention) and on human well-being.
- 18.
FAO and ITPS (2015).
- 19.
- 20.
SCBD (2016a).
- 21.
Note that the provisions of Art. 8(j) are subject to national legislation.
- 22.
SCBD (2016b).
- 23.
MA (2005), p. v.
- 24.
FAO (2015).
- 25.
These are: addressing the underlying causes of biodiversity loss by mainstreaming biodiversity across government and society (Strategic Goal A); reducing the direct pressures on biodiversity and promote sustainable use (B); improving the status of biodiversity by safeguarding ecosystems, species and genetic diversity (C); enhancing the benefits to all from biodiversity and ecosystem services (D); and enhancing implementation through participatory planning, knowledge management and capacity building (E).
- 26.
Leadley et al. (2014).
- 27.
European Commission, IASS & Umweltbundesamt (2013).
- 28.
UNEP/CBD/SBSTTA/20/13.
- 29.
UNEP/CBD/SBSTTA/15.
- 30.
UNEP/CBD/SBSTTA/7/INF/11, p. 2.
- 31.
Jeffery et al. (2010), pp. 82–83. Links (though weaker ones) also exist to the programmes of work on forest biodiversity and on dry and sub-humid lands.
- 32.
For an overview of the Initiative’s activities, see Dias and Coates (2012), pp. 9–10.
- 33.
It also acts as a connecting entity to other relevant initiatives on soil biodiversity, such as the science-driven Global Soil Biodiversity Initiative (GSBI).
- 34.
Pisupati and Prip (2015).
- 35.
See in detail at https://www.cbd.int/reports/analyzer.shtml or the syntheses UNEP/CBD/COP/10/INF/2 (2010), UNEP/CBD/WG-RI/2/INF/1 (2007) and UNEP/CBD/WG-RI/2/INF/1/Add.3 (2007). The syntheses hardly mention soils, except for the last one which focuses on the implementation of thematic programmes of work. This includes the programme on agricultural biodiversity. In this context the synthesis points out that “a few parties” in their reports mentioned assessment of soil biodiversity (ibid, para 61).
- 36.
See Jóhannsdóttir et al. (2010), p. 143. Cf. qualifying wording in the Convention text, such as the provision that parties shall “integrate, as far as possible and as appropriate, the conservation and sustainable use of biological diversity into relevant sectoral or cross-sectoral plans, programmes and policies” (Art. 6(b) CBD).
- 37.
- 38.
Jóhannsdóttir et al. (2010), p. 143.
- 39.
See publications at https://www.cbd.int/ts/.
- 40.
Cf. ELD Initiative (2015).
- 41.
The necessary number of signatories is determined in the Protocol; the Cartagena and Nagoya Protocols each specify the need for 50 parties to ratify, accept, approve or accede the Protocol.
- 42.
Namely, those 23 member states willing to commit themselves to an EU Soil Framework Directive (which was ultimately blocked by a minority of five EU countries, leading to the withdrawal of the draft directive in 2014).
- 43.
The so-called “Group of Friends (GoF) of Desertification, Land Degradation and Drought”. It includes Australia, Burkina Faso, Iceland, Lesotho, Namibia, Qatar, the Republic of Korea and Turkey.
- 44.
With regard to forestry these have been, among others, Brazil, Indonesia, Malaysia, but also Russia, Finland and Sweden. With regard to agriculture, these have included the “Miami Group” of agricultural exporters (US, Canada, Argentina etc.). In Europe, Austria, France, Germany, the Netherlands and the UK successfully blocked the draft EU Soil Protection Directive.
- 45.
Cf. Böhringer (2014).
- 46.
“Reducing Emissions from Deforestation and forest Degradation in developing countries”. The mechanism created under the UNFCCC will compensate forest-rich developing countries for not cutting down their forests.
- 47.
Wolff (2011).
- 48.
Introducing an international payment scheme analogous to REDD+ is unlikely to work in the context of international soil policy, where the incentive for states is low to compensate other countries for sustainably managing their soils. We put the example of REDD+ forward here to emphasize potential political dynamics linked to reframing an issue, not for modeling a soil instrument.
- 49.
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Wolff, F., Kaphengst, T. (2017). The UN Convention on Biological Diversity and Soils: Status and Future Options. In: Ginzky, H., Heuser, I., Qin, T., Ruppel, O., Wegerdt, P. (eds) International Yearbook of Soil Law and Policy 2016. International Yearbook of Soil Law and Policy, vol 2016. Springer, Cham. https://doi.org/10.1007/978-3-319-42508-5_11
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