Changing Ground: Handling Tensions between Production Ethics and Environmental Ethics of Agricultural Soils
Abstract
:1. Introduction
- To make sure that the general public and decision makers are fully aware of the importance of soils for the survival of humanity;
- To educate the general public on the significance of soils in relation to diverse and topical developmental goals, such as food security, poverty alleviation, climate change adaptation and mitigation, essential ecosystem services, and sustainable development;
- To help design and implement effective policies and related actions to manage soil resources in a sustainable way and to protect and conserve them for future generations;
- To enhance investing in activities that support sustainable soil management, aiming at developing and maintaining healthy soils for use by a diverse group of actors (e.g., farmers, foresters and nature conservationists);
- To strengthen any soil-related initiatives that can be interlinked with the United Nations Sustainable Development Goals and the UN Post-2015 agenda;
- To support rapidly enhancing the capacity to collect information on soil quality and to monitor changes therein, at different scales (global, regional and national).
2. Threats to Soil Quality and Health
3. Soil as a System Component Deserves Respect
4. Towards Soil Ethics
5. Introducing the Concept of Soil Telos
6. The Man-Made Telos of a Soil
7. The Natural Telos of a Soil
- A soil is able to fulfil its natural telos when it demonstrates the capacity to capture and process within several years the natural and man-made products that have accumulated or have been added during the crop cycles and fallow periods or during the use and rest periods of the vegetation (as for example for grasslands and range lands).
- The soil should do so in such a way that it can contribute to the maintenance of the water, nutrient and carbon cycles as under natural conditions and accumulate organic matter, while offering home to micro-, meso- and macro-flora and -fauna, providing the ecosystem services to the best of its ability and supporting the development aboveground and belowground of rich, functional networks and food webs towards a balanced and desirable ecosystem that is also in balance with the surrounding ecosystems (e.g., water bodies).
- Aboveground diversity and belowground diversity interact and together create a similar or improved soil fertility compared with previous years.
- Making maximum use of this soil fertility [combined health], the natural telos should also be able to express the “terroir”, the identity that is associated with the natural telos and developed into the local culture of soil management and land use, thus maintaining and enriching the soil’s legacy in which the events of ages have solidified and have created a unique and morally valuable identity.
8. Reconciling the Two Soil Teloi: Guidelines for Operationalization
- 1.
- Empowering the soil to achieve its man-made telos in a sustainable way:
- a.
- Restoring degenerated, desertified and eroded soils by planting trees, shrubs, crops and other vegetation. The loss of soils and of soil quality is often enhanced by or directly associated with the loss of vegetation growing on it. Plants reduce the impact of destructive forces (such as heavy rain), help keeping the nutrient cycles intact, support soil microorganisms and directly influence the fungal and bacterial composition of the soil in terms of species diversity and species abundance, thereby significantly affecting soil health. Replanting a suitable vegetation on degenerated or desertified soils greatly helps restoring the soils, as has been shown by the organization Commonland [75]. This is an eco-justice approach to realize the utility telos.
- b.
- Introducing agricultural policies that protect soil health and fertility and restore degraded soils. This is probably one of the most effective, yet at the same time one of the most elusive ways to promote sustainable land use. Agricultural policies can be very effective in enhancing soil quality, including soil fertility and soil health. However, agricultural policies have significantly contributed to the current decline in soil quality, in many different ways. Changes in land tenure and the feminization of agriculture world-wide are also crucial factors. For a sustainable impact of policies, trade-offs, social justice and moral choices require balanced choices on long-term objectives and effective instruments to reach those objectives [48]. Such choices require a societal debate on norms and values with all stakeholders involved, including farmers, conservationists, agrochemical industry, breeding companies and others. This is a social-justice approach to realize the utility telos.
- c.
- Introducing financial instruments to make products from soil-protecting agriculture cheaper than those from soil-degrading agriculture. Financial instruments are essential and effective tools in many policies, including the agricultural policies mentioned under b. Financial incentives determine whether a farmer can afford to farm based on soil conservation techniques and whether the consumer can afford to buy his products. Again, this is a social-justice approach to realize the utility telos.
- d.
- Expanding the previous guideline results in empowering agricultural production systems that comply with the above recommendations, for example, by effective government support for non-eroding, non-poisoning soils and their collateral environment (taxation of harmful emissions); penalties for mining too much of the nutrients from the soil (e.g., affected by the crop rotation) and other types of soil degradation; and rewards for crop rotations and actions enhancing diversity of soil life. This is a combined eco-justice and social-justice approach to realize the utility telos.
- e.
- Another way to empower these agricultural production systems is by embedding them in the local communities and the local markets, thus enhancing the resilience of these production systems and supporting the “license to produce”. This is, for example, demonstrated by the concept of Community Supported Agriculture (CSA) [76]. Another citizens’ initiative was started in the village of Duiven (Netherlands), where inhabitants are aiming to buy an area of 100 hectares of existing agricultural land, sell 5 hectares of it for building ecological houses and use the income from this to realize regenerative agriculture on the remaining 95 hectares, including a food forest [77]. A stunning, although involuntary, example of the effectiveness of local markets in this respect is the political isolation of Cuba after the collapse of the Soviet Union, which has led to a large degree of food autonomy, with most of the farms in Cuba being organic [78] and the country ranking 9th out of 164 in the Sustainable Development Index [79]. This is a social-justice approach to realize the utility telos.
- 2.
- Empowering the soil to achieve its natural telos:
- a.
- Restoring natural water courses and systems in combination with adequate vegetation. Good water management is vital for living soils and their restoration and maintenance. An impressive, positive example of this is Sekem [80], the farm and associated community and institutions in Egypt, built in the middle of the desert, starting by digging a well. A negative example is the Aral Sea [81]: when the rivers feeding it were diverted for irrigation purposes, the Aral Sea (once the fourth largest lake in the world) dried up completely, leaving extremely salty and polluted soils behind and driving the population into unemployment and poverty. This is part of an eco-justice approach to realize the natural telos.
- b.
- Acknowledging, in line with this paper, that the improvement of soil (ecosystem) fertility contributes not only to the quality of the whole food chain but also to climate balancing and carbon sequestration. (cf. Section 8, references [71,72,73,74] and the Special Report of the International Panel on Climate Change on this topic [82]). This is also part of an eco-justice approach to realize the natural telos.
- c.
- Facilitating means of feeding the soils’ ecosystems with crop residues (rich in carbon) and manure (enriched with carbon), in a way that facilitates the natural cycling and distribution of carbon, nitrogen, phosphorus, potassium, other minerals and organic matter. Natural cycles avoid imbalances of distribution, like eutrophication. This is part of an eco-justice approach to realize the natural telos.
- d.
- Screening the whole animal and plant production system for the input of toxins (pharmaceutics, animal health protection and plant protection products etc.) that harm the health of the soil ecosystem, with all its micro-, meso- and macrofauna and flora; and to remove or reduce these toxins. Today’s screening is rather insufficient as for example can be seen from vanishing meadow birds, due to declining insect populations, but also disturbance of the balance of the soil ecosystem. In several places, citizen science groups have set up a system of toxin monitoring, but to reduce the soil contamination, new, strict policy rules are required. Current policies, for instance, often do not take cumulative or even interactive effects of multiple toxins into account. This is a combination of an eco-justice and a Right of Nature approach to realize the natural telos.
- 3.
- Raising awareness about the need to reconcile the two types of teloi will benefit from:
- a.
- Reconsidering, in line with this paper, that soils should be given rights as part of nature [75], based on their natural telos and their man-made telos and acknowledging the pivotal role of soils in agriculture and ecosystems. These rights should be implemented in practice at all levels, in science, in politics, land management, nature conservation and agriculture at large (landscape, forestry etc.). This is part of a Right of Nature approach to reconcile the utility and intrinsic telos.
- b.
- Shifting the regulatory burden from non-polluting farmers (organic, biodynamic etc.) to polluting ones. This is an implementation of the “polluter pays principle”, which is strongly supported in OECD and EU countries and is a fundamental principle in US environmental law. This is part of a social-justice approach to reconcile the two types of telos.
- c.
- Introducing and stimulating the use of the criterion ‘embodied land’ for the sustainable manufacturing of any product. All aspects of any manufacturing process on earth can be expressed in terms of the quantity of land needed to make a product. ‘Embodied land’ [83] is the sum of the land area used in a given period of time to (1) produce the energy and materials required for the manufacture of a given product, (2) manufacture the product and (3) restore the resources and supplies used up. This calculation is called the “MAXergy” method, because it is a tool to maximize the ‘exergy’ of any given product. Exergy is the work potential of a system containing energy and matter. When energy or matter (including land) is used in any way, its work potential (exergy) is reduced and must be restored if the process is to be sustainable. Expressing exergy as land area (“embodied land”) will raise awareness of the need to reconcile the two soil teloi by emphasizing the quantities of land used, thus hopefully contributing to sustainable land use. This supports the realization of social justice in land use.
- 4.
- Providing monitoring tools for successful reconciliation requires:
- a.
- Making an inventory of monitoring tools for the quality assessment of soil ecosystems. Criteria defining the quality of soil ecosystems need to be established. The concept of the two soil teloi can support this. Next, assessment and monitoring methods need to be developed. This also supports the realization of eco-justice, Right of Nature and social justice in land use.
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Type | Causes * | Degradation Process | Impact on Soil Processes |
---|---|---|---|
Physical | Deforestation | Breakdown of soil structure, aggregation and porosity | Reduction in infiltration capacity; Changes in soil-water retention characteristics |
Biomass burning | Crust formation and sealing of surface | Increase in rate, intensity and quantity of runoff | |
Poor or excessive tillage or tillage under adverse conditions; Tillage up and down the slope; Excessive human, animal and machine traffic; Overgrazing | Compaction of surface and subsoil; Reduction in proportion and strength or stability of aggregates | Accelerated water and wind erosion; Increase in bulk density, resulting in poor porosity and poor infiltration; Water logging, resulting in anaerobiosis | |
Chemical | Irrigation with water of poor quality; Inadequate drainage | Salinization; Alkalization | Accumulation of base-forming cations |
Little or no use of fertilizers | Nutrient depletion/Soil mining | Decreased levels of macronutrients on exchange sites; Reduced soil organic matter content; Lower levels of nutrients in soil solution | |
Excessive use of fertilizers | Acidification; Eutrophication | Leaching and runoff of nutrients to water sources | |
Application of industrial or urban wastes | Contamination with heavy metals, other types of pollution/toxification | Excessive build-up of some heavy metals (such as Hg, Pb) or other elements (such as Al, Mn, Fe); Shifts in populations of soil-borne pathogens | |
Biological | Removal or burning of crop residues | Depletion of soil organic carbon | Reduction in N mineralization; Reduction in soil aggregation; Reduction in water retention and aeration |
Little or no use of organic inputs | Decline in abundance and diversity of soil biota | Shifts in species composition and diversity of favorable and harmful soil organisms | |
Inadequate crop rotation, continuous cropping, monoculture | Loss of soil structure | Reduction in porosity and infiltration; Reduction in activity of favorable soil biota; Increase in harmful soil biota |
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van Mansvelt, J.D.; Struik, P.C.; Bos, A.; Daub, W.; Sprangers, D.; van den Berg, M.; Vingerhoets, M.; Zoeteman, K. Changing Ground: Handling Tensions between Production Ethics and Environmental Ethics of Agricultural Soils. Sustainability 2021, 13, 13291. https://doi.org/10.3390/su132313291
van Mansvelt JD, Struik PC, Bos A, Daub W, Sprangers D, van den Berg M, Vingerhoets M, Zoeteman K. Changing Ground: Handling Tensions between Production Ethics and Environmental Ethics of Agricultural Soils. Sustainability. 2021; 13(23):13291. https://doi.org/10.3390/su132313291
Chicago/Turabian Stylevan Mansvelt, Jan Diek, Paul C. Struik, Arie Bos, Willem Daub, Diederick Sprangers, Mara van den Berg, Marieke Vingerhoets, and Kees Zoeteman. 2021. "Changing Ground: Handling Tensions between Production Ethics and Environmental Ethics of Agricultural Soils" Sustainability 13, no. 23: 13291. https://doi.org/10.3390/su132313291
APA Stylevan Mansvelt, J. D., Struik, P. C., Bos, A., Daub, W., Sprangers, D., van den Berg, M., Vingerhoets, M., & Zoeteman, K. (2021). Changing Ground: Handling Tensions between Production Ethics and Environmental Ethics of Agricultural Soils. Sustainability, 13(23), 13291. https://doi.org/10.3390/su132313291