Download Introduction to Enviromental Impact Assessment : Principles by John Glasson, Riki Therivel, Andrew Chadwick PDF

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By John Glasson, Riki Therivel, Andrew Chadwick

First released in 1994. Routledge is an imprint of Taylor & Francis, an informa corporation.

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Additional resources for Introduction to Enviromental Impact Assessment : Principles and Procedures, Process, Practice and Prospects - 2nd edition

Sample text

1988. Environmental impact assessment: theory and practice. London: Unwin Hyman. 1 Introduction Environmental impact assessment was first formally established in the USA in 1969 and has since spread, in various forms, to most other countries. In the UK, EIA was initially an ad hoc procedure carried out by local planning authorities and developers, primarily for oil- and gas-related developments. A 1985 European Community directive on EIA (Directive 85/337) introduced broadly uniform requirements for EIA to all EU Member States and significantly affected the development of EIA in the UK.

Consequently it has become an important model for other EIA systems, both because it was a radically new form of environmental policy, and because of the successes and failures of its subsequent development. Since its enactment, NEPA has resulted in the preparation of well over 10,000 full EISS and many more partial appraisals, which have influenced countless decisions and represent a powerful base of environmental information. On the other hand, NEPA is unique. Other countries have shied away from the form it takes and the procedures it sets out, not least because they are unwilling to face a situation like that in the USA, where there has been extensive litigation over the interpretation and workings of the EIA system.

The distinction between reversible and irreversible impacts is a very important one, and the irreversible impacts, not susceptible to mitigation, can constitute particular significant impacts in an EIA. It may be possible to replace, compensate for or reconstruct a lost resource in some cases, but substitutions are rarely ideal. The loss of a resource may become more serious later, and valuations need to allow for this. Some impacts can be quantified, others are less tangible. The latter should not be ignored.

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