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Ecological Footprint (EF)

“ECOLOGICAL FOOTPRINT” (EF) refers to a system of measurement developed for estimating human appropriation of ecological resources relative to biologically productive (bioproductive) land area. EFs can show how much land is needed to sustainably support a human population, nation, or a specific component of society, such as a commodity (e.g., soybeans), transportation system (e.g., auto transit), or lifestyle (i.e., a consumption pattern). The utility of footprint analysis (FA) is best understood by considering the ecology of a modern city. Urban inhabitants are concentrated within city bounds but they rely on the importation of resources and exportation of wastes to survive.

Therefore, the land area necessary to produce resources and absorb wastes far exceeds the actual geographic boundaries of the city (or nation)—in wealthy nations ecological flows may be distributed across the planet. FA provides a framework for tracking these resource and waste flows and converting them into a common metric—land area (hectares) per capita—by making use of widely available economic statistics.

The calculation of an EF is based on two key assumptions. First, it is possible to reasonably track most human resource consumption and waste generation, and translate these flows into bioproductive land areas. Second, it is possible to standardize varying land areas by weighting each according to their “potential biomass productivity.” The latter refers to production potential that is of economic interest to society, not the diverse assemblage of other organisms necessary for human survival, or biodiversity. Biodiversity is included in national and global analyses but there is much debate over how much land must be set aside. (Estimates range from 8 to 75 percent; in practice, the conservative World Commission on Environment and Development [WCED] estimate of 12 percent of bioproductive land is simply added to the footprint total for the given social unit.) EFs omit resource uses for which conversions into bioproductive land are difficult, such as the impact of local fresh water use, as well as any impact that systematically reduces the ability of ecosystems to regenerate, such as the release of nonassimilable and/or bioaccumulating chemicals (e.g., uranium, polychlorinated biphenyls [PCBs], and mercury).

Standardization Measures

The novelty of FA is in standardizing resource and waste flows in terms of bioproductive land area, instead of creating arbitrary indices or lumping together ecological and social factors. This requires analysts to distinguish between the quality of land types depending on their level of productivity. For instance, arable land is the most productive and is used for staple crops, such as wheat and corn. Pasture land is unable to support staple crops and used primarily for grazing. While pasture also produces food for human consumption, the biochemical conversion from plants to meat represents significant energy loss (a factor of 10).

Forest land represents tree farms or forests yielding timber. Built or degraded land is productive land lost to roads, buildings, and other structures. Built land is considered formerly productive because human settlement patterns indicate that arable land is ruined to accommodate infrastructure. Other types of land included are productive sea space, energyland, and biodiversity land. When calculating a footprint, resource and waste flows are first converted into one of the above land areas (in hectares) and then scaled by multiplying by an equivalence factor (EQ), also in hectares. EQs express differences in land productivity compared to world average productivity (e.g., in 1999 arable land had an EQ of 2.1 and pasture land 0.5). World average productivity, and consequently the productivity of each above land type, is recomputed each year to account for reductions in resource stocks, such as desertification, fishery collapse, urbanization, and so on.

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