pollutants were then introduced as fac<strong>to</strong>rs that reduce crop growth, thereby determining the‘actual’ yield. The notions of ‘potential’, ‘attainable’ and ‘actual’ therefore differentiateclearly the fac<strong>to</strong>rs that define, limit or reduce yield, respectively (Bouman et al., 1996; vanIttersum and Rabbinge, 1997). (‘Available’ was later described in the Report “Realizing thepromise and potential of African agriculture” (InterAcademy Council, 2004) <strong>to</strong> recognise thata proportion of the actual harvest was lost post-harvest, resulting in a further reduced amoun<strong>to</strong>f food that is actually available for human consumption.)This production ecology approach was based on the concept of a single limiting fac<strong>to</strong>r which,once overcome, would allow growth <strong>to</strong> increase until it was restricted by another limitingfac<strong>to</strong>r (the ‘minimum function’). A number of crop, crop-soil and crop-soil-pest modellingapproaches have been developed relating <strong>to</strong> a range of production situations, i.e. potential,water and/or nutrient-limited (van Ittersum et al., 2003). Differentiating the ‘potential’,‘attainable’ and ‘actual’ concepts is very useful for application in other areas of researchwhere there also is a set of limiting fac<strong>to</strong>rs. In the case of carbon sequestration in soils, forinstance, soil mineralogy, net primary production and erosion are among major defining,limiting and reducing fac<strong>to</strong>rs, respectively (Ingram and Fernandes, 2001). A key point aboutthis approach is that interactions between limiting fac<strong>to</strong>rs are additive not multiplicative.Dalgaard et al. (2003) define agroecology as “the study of the interactions between plants,animals, humans and the environment within agricultural systems”. The general construct ofagroecology is therefore broader than the initial production ecology concept, which wasbased on a single limiting fac<strong>to</strong>r. It does however draw on this, but includes also theecological notions of interconnectivity, community behaviour and spatial organisation. Itbuilds on the community ecology notion of Clements (i.e. including “higher hierarchicallevels than the organism [the plant]”), and the worldview of Tansley, which included bothbiotic entities and their environment (Dalgaard et al., 2003). In this regard it is also alignedwith a fuller notion of production ecology (i.e. including the interactions with lives<strong>to</strong>ck), butincludes integrative studies not only within agronomy and ecology but also includingenvironmental science more generally. Interdisciplinarity and scaling across spatial levels areboth central tenets and the broad agroecology concept thereby helps move the debate <strong>to</strong>wardsthe needs discussed in Paper 2, and thus <strong>to</strong>wards the broader food security agenda. (Thefurther broadening of both concepts is discussed below.)It is important <strong>to</strong> note that the ‘eco’ letters in the word ‘agroecology’ do not denote – letalone advocate – a particular approach, as recommended by De Schutter in his SpecialRapporteur report on the right <strong>to</strong> food, presented <strong>to</strong> the UN General Assembly in December2010 (De Schutter, 2010). His argument that agroecology “seeks ways <strong>to</strong> enhance agriculturalsystems by mimicking natural processes” is incorrect; agroecology does not seek <strong>to</strong> mimic‘natural processes’ but apply ecological principles <strong>to</strong> help understand how agriculturalsystems operate and can be better managed. While “integrating crops and lives<strong>to</strong>ck;diversifying species and genetic resources in agroecosystems over time and space; andfocusing on interactions and productivity across the agricultural system, rather than focusingon individual species” can all be accommodated within agroecological concepts, its “core114
principles” do not “include recycling nutrients and energy on the farm, rather thanintroducing external inputs”. Agroecology does not advocate organic or low-inputagriculture. It is a board concept, providing a framework for investigating the ways of linkinga range of inputs (germplasm, nutrients, pesticides, water, energy) with the goods andservices we seek from agricultural systems in the context of the natural resource base.Both the production ecology and agroecology approaches have been further developed <strong>to</strong>consider fac<strong>to</strong>rs operating at higher spatial levels, i.e. farm, landscape and even region.Examples include integrated approaches for agro-ecological zonation and regional yieldforecasting (Bouman et al., 1996); scenario studies for exploring the effect of environmentalor socioeconomic changes on agriculture such as the ‘Grounds for Choices’ study(Netherlands Scientific Council for Government Policy, 1992; Rabbinge and Van Latesteijn,1992); for ex-ante evaluation of public policies for sustainable agriculture at landscape level(Parra-López et al., 2009); and for exploring multi-scale trade-offs between natureconservation, agricultural profits and landscape quality (Groot et al., 2007). Interactions withlives<strong>to</strong>ck (i.e. the whole farming system) are also critically important in many parts of theworld, and particularly in helping farmers cope with uncertainty regarding future threats andpotentials (Darnhofer et al., 2010). The boundary between the two approaches are in effectbecoming less distinct as researchers move <strong>to</strong>wards addressing problems at regional <strong>to</strong> globallevels, integrating other environmental objectives in addition <strong>to</strong> food production.While the production ecology and agroecology concepts have therefore moved well beyondfood production at local level <strong>to</strong>wards food availability at higher levels neither, however,addresses the broader issues underpinning food security. For instance, affordability, foodallocation and cultural norms, food preferences and the social and cultural functions of food,and food safety, all need <strong>to</strong> be fac<strong>to</strong>red in. This needs additional analyses of the consequencesof human activities as a chain of effects through the ecosystem and human social system.This is the realm of human ecology, encompassing elements of sociology concerned with thespacing and interdependence of people and institutions (Marten, 2001). As with bothproduction ecology and agroecology, the study of human ecology is composed of conceptsfrom ecology including interconnectivity, community behaviour, and spatial organisation.‘Interaction’ is a fundamental concept of human ecology and is a function of scale, diversityand complexity. Together with political economy and entitlement relations, human ecologyhas been seen for some time as a causal structure of food system vulnerability, and hencefood insecurity (Bohle et al., 1994). Concepts from human ecology are very relevant for foodsystems analyses given the importance of the linkages between the wide range of ac<strong>to</strong>rsinvolved and the outcomes of their varied activities.‘<strong>Food</strong> system ecology’ based on integrating concepts<strong>Food</strong> security planning can be enhanced by integrating concepts from production ecology,agroecology and human ecology with concepts of food systems and scales.Understanding the interactions between the many activities and associated stakeholder115
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Figure 3 Outcomes for 10 variables
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Figure 4 Nine ‘planetary boundari
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Parry et al., 2005). Conducting foo
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