Review of land use impact methodologies

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Abstract

A review was performed of existing approaches on land use methods for LCA. Two main questions arise: how does land occupation relate to (irreversible) land changes, and what indicators are to be used to describe land use impacts. Most approaches aim at a single or limited number of indices for land use impacts, for data availability reasons. Vascular plant species density is the most common basis for an indicator. Methods using many more indicators may be seen as future sophistications, when data is available over the whole life cycle. For silviculture and agriculture crops multi-indicator scores may be applicable now to compare management techniques. Land use efficiency measured by m2.y is presently seen as the inventory step of land occupation impact assessment, but may also be a separate issue. Land management techniques in fact influence long-term changes and should be assessed as such, or not quantified at all. Further discussion and harmonisation is however required.

Introduction

Land use has recieved increasing attention in life cycle assessment (LCA). In the Dobris Assessment of the EU [1] the issue is mentioned as a separate problem, being a main cause of ecosystem degradation. But recently there have been structural changes in land use which are beneficial to ecosystem development. Both kinds of impacts need a quantitative basis to ensure this important contributor to ecosystem quality is dealt with adequately. This article is a review of the developments since about 5 years ago, based on LCA literature on land use.

Section snippets

General framework and terminology for land use impacts in LCA

Land use impacts in LCA are related to the area of land used, generally in combination with the time required to produce a certain output. These data are generally combined with qualifications of the land type changed or under use. The rationale for this is that the area and time required to produce a certain output reveals something about the land use effectivity or productivity, whereas the quality shows how seriously a land use change or a certain land occupation should be considered from an

Land use impacts assessment approaches

Three groups of assessment systems for land use impacts in LCA can be distinguished [6], although they are to a certain extent overlapping. The groups are chosen according to how the methods deal with the cause–effect chain of land use impacts. These are:

  • 1.

    functional approach

  • 2.

    land use classes

  • 3.

    key indicators

Next to this grouping, indicator systems vary in their dealing with a reference state to relate a certain score to background information, and on which type of impacts are considered. These

Discussion

It is worth considering the cause effect chain in relation to the different approaches (see the figure relating to this cause effect chain in [6, Fig. 2], discussed elsewhere in this issue). All indicators up until now relate to the safeguard subject Ecosystem Quality, according to the terminology of [38], [39]. According to [6] the impacts of water extractions on ecosystems can be expressed using the same indicators for Ecosystem Quality. For vascular plant species density and (f)NPP, data

Conclusions

In conclusion, once the ambition is to quantify land use impacts in LCA the starting point should be a simple list of indicators. Further sophistication is then possible, when required in discussions on land use issues. Most indicators being suggested relate to biodiversity, and are measured in terms of vascular plant species diversity, due to lack of more extensive data. Only two authors apply biomass-related indicators, to address the issue of life support. The recovery time seems a possible

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